Christopher R. DeRolph
Oak Ridge National Laboratory
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Publication
Featured researches published by Christopher R. DeRolph.
Proceedings of the National Academy of Sciences of the United States of America | 2017
Ryan A. McManamay; Sujithkumar Surendran Nair; Christopher R. DeRolph; Benjamin L. Ruddell; April Morton; Robert N. Stewart; Matthew J. Troia; Liem T. Tran; Hyun Kim; Budhendra L. Bhaduri
Significance We introduce a unique and detailed data-driven approach that links cities’ hard infrastructures to their distal ecological impacts on streams. Although US cities concentrate most of the nation’s population, wealth, and consumption in roughly 5% of the land area, we find that city infrastructures influence habitats for over 60% of North America’s fish, mussel, and crayfish species and have contributed to local and complete extinctions in 260 species. We also demonstrate that city impacts are not proportionate to city size but reflect infrastructure decisions; thus, as US urbanization trends continue, local government and utility companies have opportunities to improve regional aquatic ecosystem conditions outside city boundaries through their hard infrastructure policies. Cities are concentrations of sociopolitical power and prime architects of land transformation, while also serving as consumption hubs of “hard” water and energy infrastructures. These infrastructures extend well outside metropolitan boundaries and impact distal river ecosystems. We used a comprehensive model to quantify the roles of anthropogenic stressors on hydrologic alteration and biodiversity in US streams and isolate the impacts stemming from hard infrastructure developments in cities. Across the contiguous United States, cities’ hard infrastructures have significantly altered at least 7% of streams, which influence habitats for over 60% of North America’s fish, mussel, and crayfish species. Additionally, city infrastructures have contributed to local extinctions in 260 species and currently influence 970 indigenous species, 27% of which are in jeopardy. We find that ecosystem impacts do not scale with city size but are instead proportionate to infrastructure decisions. For example, Atlanta’s impacts by hard infrastructures extend across four major river basins, 12,500 stream km, and contribute to 100 local extinctions of aquatic species. In contrast, Las Vegas, a similar size city, impacts <1,000 stream km, leading to only seven local extinctions. So, cities have local policy choices that can reduce future impacts to regional aquatic ecosystems as they grow. By coordinating policy and communication between hard infrastructure sectors, local city governments and utilities can directly improve environmental quality in a significant fraction of the nation’s streams reaching far beyond their city boundaries.
PLOS ONE | 2018
Ryan A. McManamay; Matthew J. Troia; Christopher R. DeRolph; Arlene Olivero Sheldon; Analie Barnett; Shih-Chieh Kao; Mark G. Anderson
Describing the physical habitat diversity of stream types is important for understanding stream ecosystem complexity, but also prioritizing management of stream ecosystems, especially those that are rare. We developed a stream classification system of six physical habitat layers (size, gradient, hydrology, temperature, valley confinement, and substrate) for approximately 1 million stream reaches within the Eastern United States in order to conduct an inventory of different types of streams and examine stream diversity. Additionally, we compare stream diversity to patterns of anthropogenic disturbances to evaluate associations between stream types and human disturbances, but also to prioritize rare stream types that may lack natural representation in the landscape. Based on combinations of different layers, we estimate there are anywhere from 1,521 to 5,577 different physical types of stream reaches within the Eastern US. By accounting for uncertainty in class membership, these estimates could range from 1,434 to 6,856 stream types. However, 95% of total stream distance is represented by only 30% of the total stream habitat types, which suggests that most stream types are rare. Unfortunately, as much as one third of stream physical diversity within the region has been compromised by anthropogenic disturbances. To provide an example of the stream classification’s utility in management of these ecosystems, we isolated 5% of stream length in the entire region that represented 87% of the total physical diversity of streams to prioritize streams for conservation protection, restoration, and biological monitoring. We suggest that our stream classification framework could be important for exploring the diversity of stream ecosystems and is flexible in that it can be combined with other stream classification frameworks developed at higher resolutions (meso- and micro-habitat scales). Additionally, the exploration of physical diversity helps to estimate the rarity and patchiness of riverscapes over large region and assist in conservation and management.
Science of The Total Environment | 2016
Christopher R. DeRolph; Michael P. Schramm; Mark S. Bevelhimer
Uncertainty about environmental mitigation needs at existing and proposed hydropower projects makes it difficult for stakeholders to minimize environmental impacts. Hydropower developers and operators desire tools to better anticipate mitigation requirements, while natural resource managers and regulators need tools to evaluate different mitigation scenarios and order effective mitigation. Here we sought to examine the feasibility of using a suite of multi-faceted explanatory variables within a spatially explicit modeling framework to fit predictive models for future environmental mitigation requirements at hydropower projects across the conterminous U.S. Using a database comprised of mitigation requirements from more than 300 hydropower project licenses, we were able to successfully fit models for nearly 50 types of environmental mitigation and to apply the predictive models to a set of more than 500 non-powered dams identified as having hydropower potential. The results demonstrate that mitigation requirements are functions of a range of factors, from biophysical to socio-political. Project developers can use these models to inform cost projections and design considerations, while regulators can use the models to more quickly identify likely environmental issues and potential solutions, hopefully resulting in more timely and more effective decisions on environmental mitigation.
Reviews in Fish Biology and Fisheries | 2016
Brenda M. Pracheil; Christopher R. DeRolph; Michael P. Schramm; Mark S. Bevelhimer
Environmental Science & Policy | 2016
Michael P. Schramm; Mark S. Bevelhimer; Christopher R. DeRolph
Ecology and Evolution | 2015
Christopher R. DeRolph; Stacy A. C. Nelson; Thomas J. Kwak; Ernie F. Hain
Archive | 2016
David B. Watson; Scott C. Brooks; Teresa Mathews; Mark S. Bevelhimer; Christopher R. DeRolph; Craig C. Brandt; Mark J. Peterson; Richard Ketelle
Endangered Species Research | 2016
Brenda M. Pracheil; Ryan A. McManamay; Mark S. Bevelhimer; Christopher R. DeRolph; Glenn F. Cada
Archive | 2017
Scott C. Brooks; Virginia Eller; Johnbull O. Dickson; Jennifer E. Earles; Kenneth Lowe; Tonia L. Mehlhorn; Todd A. Olsen; Christopher R. DeRolph; David Watson; Debra Phillips; Mark J. Peterson
Archive | 2018
Shelaine L. Curd; Christopher R. DeRolph; Ryan A. McManamay; Esther S. Parish; Brenda M. Pracheil; Brennan T. Smith